Composition and diversity of anurans from rock outcrops in the Caatinga Biome, Brazil - Biotaxa

 
Composition and diversity of anurans from rock outcrops in the Caatinga Biome, Brazil - Biotaxa
Herpetology Notes, volume 11: 189-195 (2018) (published online on 20 February 2018)

       Composition and diversity of anurans from rock outcrops
                    in the Caatinga Biome, Brazil

          Déborah Praciano de Castro1,3,4,*, João Fabrício Mota Rodrigues2,4, Daniel Cassiano Lima3,4 and
                                            Diva Maria Borges-Nojosa1,4

Abstract. We provide a list of anurans from an open area of Caatinga stricto sensu, state of Ceará, Brazil. Fieldwork was
conducted from July 2010 to July 2011 by sampling the reproductive sites. In total, 19 frog species were recorded, distributed
in 13 genera and five families. The number of species found in our study represents 34.5% of the 55 anurans registered for the
state of Ceará. The recorded anurofauna is widely distributed and is typical of open areas. One of the species found in our work
is more associated with the Cerrado biome (D. rubincundulus). The group of species we recorded represents a subset of the
species pool of the Caatinga. Our paper contributes to the knowledge of lowland Caatinga sites outside protected areas.

Keywords: amphibians, semiarid region, richness, biodiversity

Introduction                                                     are found in areas occupied by this vegetation (Borges-
                                                                 Nojosa et al., 2010).
  The Caatinga, along with the Cerrado and Chaco, is
                                                                   Amphibians comprise one of the groups with greatest
classified as a Seasonally Dry Tropical Forest and is
                                                                 morphological and physiological variation among
considered the only biome located entirely within the
                                                                 vertebrates (Duellman and Trueb, 1994), covering
Brazilian territory (Oliveira and Diniz-Filho, 2010).
                                                                 approximately 7643 species, distributed mainly in
This biome is subject to a climatic regime of intense and
                                                                 the tropics (Frost, 2017). Among the amphibians, the
irregular rainfall distributed between three to six months
                                                                 order Anura is the most abundant (Vieira et al., 2007),
of the year, presents shallow soils with a savannah
                                                                 and the families Hylidae and Leptodactylidae are the
vegetation, including xerophytic, shrubby, and thorny
                                                                 most representative in the Neotropics (Bertoluci et al.,
deciduous physiognomies (Oliveira and Diniz-Filho,
                                                                 2007). Hylids predominate in forested environments
2010). In recent decades, natural areas of Caatinga have
                                                                 and leptodactylids concentrate mainly in open areas
been under intense degradation, and approximately
                                                                 (Arzabe, 1999).
62% of zones susceptible to desertification in Brazil
                                                                   Heyer (1988) identified the Caatinga as one of the
                                                                 least known biomes of South America, with extensive
                                                                 areas lacking information on composition, natural
                                                                 history, and ecology of amphibians. Although the
1
  Programa de Pós- Graduação em Ecologia e Recursos              number of studies is still much lower when compared
   Naturais, Departamento de Biologia, Universidade Federal      with Brazilian forested areas (Loebmann and Haddad.,
   do Ceará, Campus do Pici, 60.455-970, Fortaleza- CE, Brasil   2010), there has been an increase in the number of
2
  Programa de Pós-Graduação em Ecologia e Evolução,
                                                                 studies conducted in areas of Caatinga (e.g., Arzabe.,
   Departamento de Ecologia, Instituto de Ciências Biológicas,
                                                                 1999; Borges-Nojosa and Cascon., 2005; Garda et al.,
   Universidade Federal de Goiás, Cx. P. 131, 74001-970,
   Goiânia, GO, Brasil                                           2013; Santana et al., 2015).
3
  Universidade Estadual do Ceará, Av. Monsenhor Tabosa, CEP        In this paper, we present new information on the
   62500-000 Itapipoca, CE, Brasil                               composition and diversity of an anuran assemblage
4
  Núcleo Regional de Ofiologia da UFC (NUROF-UFC),               from rock outcrops in the Caatinga.
   Departamento de Biologia, Universidade Federal do Ceará,
   Campus do Pici, Bloco 905, Cep 60.440-554, Fortaleza,         Materials and Methods
   Ceará, Brasil
* Corresponding author. E-mail: deborahpraciano@gmail.com          Study area.—This study was conducted at the Sítio
Composition and diversity of anurans from rock outcrops in the Caatinga Biome, Brazil - Biotaxa
190                                                                                      Déborah Praciano de Castro� et al.

Figure 1. Climatic diagram Walter and Lieth (temperature and rainfall x months), during the study period (2010-2011) for Sítio
Paleontológico Lajinhas, Itapipoca, Ceará, Brazil. R environment, package climatol (R Development Core Team, 2013).

Paleontológico Lajinhas (SPL; Lajinhas Paleontological          • “Lagoa da Aposta” (LA) (3.41616667S/
site), in the municipality of Itapipoca, Ceará,                   39.69219444W) (Fig 2B): Area of low topography,
northeastern Brazil (3.41770833S/ 39.69210278W).                  with a maximum height of 1.5 m. It has five lentic
Caatinga vegetation is predominant in the area, with              and temporary ponds up to five square meters and
forest and shrub species of the Cactaceae, Fabaceae               small puddles on the rock surface. The vegetation
and Euphorbiaceae families (Ximenes, 2008). The                   presents few Cactaceae and Bromeliaceae species,
homogeneity of the landscape is often interrupted by              and scrub vegetation, but also a massive presence of
granite rock outcrops, very common in certain areas of            macrophytes inside the ponds, completely covering
Caatinga and locally called lajeiros (Ximenes, 2008).             the surface of two of them.
The study area has a hot semiarid climate with high             • “Lajeiro da Jia” (LJ) (3.41594444S/ 39.69083333W)
temperatures and low annual rainfall (from 600 to                 (Fig 2C): It has five temporary pools with a maximum
800 mm), which is concentrated from January to June,              depth of 8 m, approximately. There is no scrub
with the remaining months of the year being very dry              vegetation on the lajeiro, but it accumulates large
(Funceme, 2011) (Fig 1).                                          amount of aquatic weeds during the rainy season.
                                                                In order to improve the sampling, animals found
  Data collection.�—Fieldwork was conducted monthly               between the lajeiros were also recorded (Fig 2D).
from July 2010 to July 2011, consisting of three days           The abundance of each species was estimated using an
per month. We conducted active and acoustic surveys               active search method at the reproductive sites (Scott
with three observers at each study site that were                 and Woodward, 1994). All individuals on the perimeter
sampled during the daytime (8:00 to 12:00 am each                 of the water bodies were recorded, including non-
day) and at night (18:00 pm to 1:00 am each day, or               active ones. We used toe clipping (Ferner, 2007) to
while vocalizing animals were heard), with a total effort         mark all individuals. The monthly occurrence of the
of 429 hrs/person.                                                species was assessed using the method of Silveira-
  This study was conducted at three lajeiros (LC, LA              Neto et al. (1976), which classifies the species as:
and LJ, see detailed description below). The distances            constant, when they are present in more than 50%
between these areas are: LC/ LA= 700 m; LC/LJ = 800               of samples; accessory, those present between 25% to
m; LA/LJ= 200 m (Fig 2):                                          50% of samples; and occasional, when found in less
• “Lajeiro do Criminoso” (LC) (3.42183333S/                       than 25% of the samples. Specimens were deposited
   39.69422222W) (Fig 2A): The largest rocky outcrop              in the Coleção de Herpetologia da Universidade
   in the study area, up to 10 m high. It has about 40            Federal do Ceará (CHUFC; Herpetological
   temporary pools of different sizes, and two ponds              Collection of the Federal University of Ceará) and the
   with accumulated sediment, with vast vegetation                species nomenclature follows Duellman et al. (2016)
   encrusted in sediment and rock crevices.                       and Frost (2017).
Composition and diversity of anurans from rock outcrops in the Caatinga Biome, Brazil - Biotaxa
Composition and diversity of anurans from rock outcrops, Brazil                                                      191

Figure 2. Sampled Lajeiros in Sítio Paleontológico Lajinhas, Itapipoca, Ceará, northeastern Brazil. A: Lajeiro do Criminoso
(rainy season); B- Lagoa da Aposta (rainy season); C- Lajeiro da Jia (dry season); D- Area between lajeiros (rainy season).

  Statistical analyzes.� —To determine sampling                (LJ) and the areas between lajeiros showed an equal
efficiency, we constructed species richness curves             number of species (11) (Table 2). The accumulation
(Krebs, 1999). Species richness of the sampled area was        curve suggested that more species may be found at these
estimated by extrapolation of a species accumulation           sites, and Chao 1 and Jackknife 1 estimated the richness
curve using Jackknife 1 and Chao 1 estimators, with            of the area to be between 20 - 23 species (Fig 3).
500 randomizations in the software Estimates, version            The species with the highest abundances were, in
7.5 (Colwell, 2005). To analyse the relative abundance         decreasing order: Pseudopaludicola mystacalis (Cope,
of anurans, we built a Whittaker plot and the species          1887) (n = 603); Pleurodema diplolister (Peters, 1870)
abundance distribution was fitted to four models of            (n = 293); Physalaemus albifrons (Spix, 1824) (n =
abundance (Broken stick, log normal, logarithmic and           135); and Scinax x-signatus (Spix, 1824) (n = 131).
geometric series) (Magurran, 2011), which were tested          With regard to the species abundance distribution,
using a chi-square test in the program PAST (Hammer            the assemblage fit best to the log-normal model (Chi-
et al., 2001).                                                 square = 2.73; p= 0.43) (Fig 4). Pseudopaludicola
                                                               mystacalis was the most frequent species, followed by
Results                                                        Leptodactylus vastus A. Lutz, 1930, and they occurred
                                                               in all sampling months and at all sampling points (P =
  We found 19 species distributed in 13 genera and five
                                                               100%). Considering rate of occurrence, 47% of species
families: Bufonidae (2), Odontophrynidae (1), Hylidae
                                                               were occasional, 21% were regarded as accessory and
(6), Leptodactylidae (9) and Microhylidae (1). The
                                                               32% had a constant occurrence (Table 1).
Lajeiro do Criminoso (LC) site had the highest richness
(15 species). The Lagoa da Aposta (LA), Lajeiro da Jia
192                                                                                     Déborah Praciano de Castro� et al.

Figure 3. Species       accumulation curves and diversity        Figure 4. Whitakker diagram for the distribution of abundance
estimators for anuran species at the three lajeiros and the      of the anuran assemblage from Sítio Paleontológico Lajinhas,
sampled area between lajeiros from July 2010 to July 2011.       Itapipoca, Ceará. The bars represents relative abundance
The observed curve is represented by the solid line and curves   (%) and top numbers the total abundance of individuals
with symbols represent the estimators (Chao 1: squares and       of each species collected and observed during the study
Jackknife 1: triangle), all generated using Estimates 7.5        period. Species: Pmist (Pseudopaludicola mystacalis);
(Colwell, 2005) after 500 randomizations.                        Pdipl (Pleurodema diplolister); Sxsig (Scinax x-signatus);
                                                                 Lvast (Leptodactylus vastus); Lfusc (Leptodactylus fuscus);
                                                                 Rjimi (Rhinella jimi); Pcuvi (Physalaemus cuvieri); Lmacr
                                                                 (Leptodactylus macrosternum); Ltrog (Leptodactylus
                                                                 troglodytes); Pcrist (Proceratophrys cristiceps); Pnord
Discussion
                                                                 (Phitecopus nordestinus) Rgran (Rhinella granulosa);
  We found that the assemblage of frog species in the            Epiau (Elachistocleis piauiensis); Drubi (Dendropsophus
“Sítio Paleontológico Lajinhas” follows the pattern              rubincundulus); Ttyph (Trachycephalus typhonius); Cgree
                                                                 (Corythomanthis greeningi); Brani (Boana raniceps).
repeated in different regions of the Caatinga, with species
of wide distribution and few endemic species of the
biome (Cascon, 1987; Arzabe, 1999). This distribution
pattern is also found in other semi-arid environments
in the world, probably because the species of wide               and Loebmann, 2016). This is, therefore, the second
distribution are less susceptible to climatic instability of     record of D. rubincundulus for Caatinga stricto sensu
the semiarid region (Chesson et al., 2004; Oliveira and          areas in Ceará state.
Diniz-Filho, 2010).                                                All species recorded in this study are cited in the IUCN
  Hylidae and Leptodactylidae had similar proportions            Red List and Brazilian List of Threatened Species as
of species richness in the present study. Caatinga               Least Concern (LC). The number of anuran species
areas commonly have a great number of species of                 found in our study represents 34.5% of the 55 anurans
the Leptodactylidae family, due to their adaptations             registered by Roberto and Loebmann (2016) for the state
to climate unpredictability (Cascon and Langguth,                of Ceará. The species richness found here is similar to
2016). Our findings are similar to those found in                that recorded for other areas of Caatinga stricto sensu in
other studies conducted in the Caatinga (Arzabe,                 the state of Ceará: Serra das Almas (22 species, Borges-
1999; Vieira et al., 2007) and are probably associated           Nojosa and Cascon, 2005), Vale do Jaguaribe (19 species,
with the environmental dynamics of the Caatinga.                 Santana et al., 2015), and slightly lower than that found
Species inhabiting large geographic areas can tolerate           for mountain and coastal regions in the state (Borges-
a wider range of environmental conditions and exhibit            Nojosa, 2007, Borges-Nojosa et al., 2010, Loebmann
high reproductive rates in environments with marked              and Haddad, 2010, Ribeiro, et al., 2012, Borges-Leite et
instability (Oliveira and Diniz-Filho, 2010). However,           al., 2014, Cascon et al., 2014). Roberto and Loebmann
one of the species found in our work is more related             (2016) recorded only two species of anurans for the
with the Cerrado biome (D. rubincundulus) and was                municipality of Itapipoca (L. macrosternum and P.
registered in the state of Ceará for cerrado areas in the        mystacalis). Thus, our paper presents the first complete
Ibiapaba Plateau and caatinga area in the municipality of        list of anurans for this municipality.
Morada Nova (Loebmann and Haddad, 2010; Roberto
Composition and diversity of anurans from rock outcrops, Brazil                                                                          193
Table 1. Frog species recorded in the Sítio Paleontológico Lajinhas, Itapipoca, Ceará state, northeastern Brazil, from July 2010
to July 2011: N= total abundance; FO- Monthly frequency of occurrence; CI- Constancy index; Ac- Accessory; Co- Constant;
Oc- occasional. Sampled points: LC- Lajeiro do Criminoso; LA- Lagoa da Aposta; LJ- Lajeiro da Jia; EP Extra Points; DG-
Geographic distribution: CA- Endemic Caatinga; CE- Cerrado with occasional occurrence in other domains; CC- Caatinga and
Cerrado; WO- Widespread occurrence in Brazil; UD- Unknown Distribution.

  F    FAMILY             SPECIES                                              N      FO       CI                POINT              DG
                                                                                                      LC    LA     LJ      EP
      Bufonidae           Rhinella granulosa (Spix, 1824)                      7      46%      Ac     X     X      0       0        WO
                          Rhinella jimi (Stevaux, 2002)                        48     61%      Co     X     X      X       X        WO
      Odontophrynidae     Proceratophrys cristiceps (Muller, 1884)             20     15%      Oc     X     0      0       X        WO
      Hylidae             Corytomanthis greeningi Boulenger, 1896              1      7%       Oc     0     0      X       0        CA
                          Dendropsophus rubincundulus (Reinhdart and           2      15%      Oc     X     0      0       0        CE
                          Lutken, 1862, "1861)
                          Boana raniceps (Cope, 1862)                          1      7%       Oc     0     X      0       0        WO
                          Pithecopus nordestinus (Caramaschi, 2006)            12     30%      Oc     X     X      0       X        CA
                          Scinax x-signatus (Spix, 1824)                       131    61%      Co     X     X      X       X        WO
                          Trachycephalus typhonius (Linnaeus, 1758)            1      7%       Oc     0     0      X       0        WO
      Leptodactylidae     Leptodactylus fuscus (Schneider, 1799)               50     61%      Co     X     X      0       X        WO
                          Leptodactylus macrosternum Miranda Ribeiro, 1926     37     61%      Co     X     X      X       X        WO
                          Leptodactylus gr. latrans                            5      23%      Oc     X     0      0       0        UD
                          Leptodactylus troglodytes A.Lutz, 1926               27     7%       Oc     X     0      0       0        CC
                          Leptodactylus vastus A. Lutz, 1930                   96     100%     Co     X     X      X       X        CC
                          Physalaemus albifrons (Spix, 1824)                   135    46%      Oc     X     X      X       X        CC
                          Physalaemus cuvieri Fitzinger, 1826                  44     23%      Oc     X     0      X       X        WO
                          Pleurodema diplolister (Peters, 1870)                293    46%      Ac     X     X      X       X        CA
                          Pseudopaludicola mystacalis (Cope, 1887)             603    100%     Co     X     X      X       X        WO
      Microhylidae        Elachistocleis piauiensis Caramaschi and Jim, 1983   3      15%      Oc     0     0      X       0        CC

                                                                                                                                                  1
  The accumulation curve did not reach an asymptote,                       knowledge of the diversity of these areas. New studies
indicating that the richness of the surveyed area may                      are required to improve the characterization of the
be greater than that found in this study. Considering                      biodiversity of the region and for the conservation of
abundance, four of the 19 species represented 76.69%                       the Caatinga biome.
of all individuals collected, while the other 15 recorded
species comprised only 23.30% of the total. The                            Acknowledgments: The authors are grateful to Tiago A. Sousa,
                                                                           Wadson A. M. Frota, Rafaela Santos and Wallony Brito for help
dominance of a few species over the others shows an
                                                                           during the fieldwork; Carla Rezende for initial critiques of the
inverted “J” distribution in the Whittaker’s distribution
                                                                           manuscript and three anonymous reviewers for their important
curve of abundances (log-normal pattern). According to                     and expressive suggestions. We also would like to acknowledge
Magurran (2011), most biological assemblages follow                        the Instituto Chico Mendes de Conservação da Biodiversidade
this pattern, which can be explained by the central limit                  (ICMBio) for the collecting license (Number 25458-2) and the
theory, which states that if a large number of independent                 Coordenação de Aperfeiçoamento de Pessoal de Nível Superior
factors, such as climate, acts on a certain variable (e.g.                 (CAPES) for the master scholarship conceded to Déborah Praciano
                                                                           de Castro.
abundance), it tends to acquire a normal distribution.
The log-normal model found here is identified as the
                                                                           References
one in which most species have intermediate abundance
and few have small or large abundance (Magurran,                           Arzabe, C. (1999): Reproductive activity patterns of anurans in two
2011).                                                                       different altitudinal sites within the Brazilian Caatinga. Revista
                                                                             Brasileira de Zoologia 3: 851-864.
  Descriptive studies are very important for the
                                                                           Bertoluci, J., Brassaloti, R.A., Ribeiro Jr., W.J., Faria, M.V.N.V.
characterization of the diversity of anurans in Ceará                        and Sawakuchi, H. (2007): Composição de espécies e similari-
state, especially in lowland Caatinga sites outside                          dades entre taxocenoses de anuros de áreas florestais do Sudeste
protected areas. Our paper contributes to increase the                       do Brasil. Scientia Agricola 64: 364-374.
194                                                                                                Déborah Praciano de Castro� et al.

Borges-Leite, M.J., Rodrigues, J.F.M., Borges-Nojosa, D.M.               Garda, A.A., Costa, T.B., Santos-Silva, C.R., Mesquita, D.O., Far-
   (2014): Herpetofauna of a coastal region of Northeastern Brazil.         ia, R.G., Conceição, B.M., Silva, I.R.S., Ferreira, A.S., Rocha,
   Herpetology Notes 7: 405-413.                                            S.M., Palmeira, C.N.S., Rodrigues, R., Ferrari, S.F.,Torquato,
Borges-Nojosa, D.M. (2007): Diversidade de anfíbios e répteis               S. (2013): Herpetofauna of protected áreas in the Caatinga I:
   da serra de Baturité, Ceará. In:. Diversidade e conservação da           Raso da Catarina Ecological Station (Bahia, Brazil). CheckList
   biota na serra de Baturité, Ceará. pp. 225-247. Oliveira, T.S.           9: 405-414.
   and Araújo, F.S., Eds, Universidade Federal do Ceará, Coelce,         Hammer., Harper, D.A.T., Ryan, P.D. (2001): Past: Paleontological
   Fortaleza.                                                               Statistics Software Package for Education and Data Analysis.
Borges-Nojosa, D.M., Prado, F.M.V., Borges-Leite, M.J., Gurgel              Paleontological Electronic 4: 9.
   Filho, N.M. Bacalini, P. (2010): Avaliação do impacto do              Heyer, R.H. (1988): On frog distribution patterns east of the Andes.
   manejo florestal sustentável na herpetofauna de duas áreas de            In: Proceedings of a Workshop on Neotropical Distribution Pat-
   caatinga no estado do Ceará. In: Uso sustentável e conservação           terns. pp. 245-273. Vanzolini, P.E., Heyer, R.H., Eds, Academia
   dos recursos florestais da caatinga. pp. 315-329. Gariglio, M.A.,        Brasileira de Ciências, Rio de Janeiro, Brasil.
   Sampaio, E.V.S.B., Cestaro, L.A. and Kageyama, P.Y., Eds,             Krebs, C.J. (1999): Ecological Methodology. Menlo Park: Addison
   Ministério do Meio Ambiente.                                             Wesley Educational Publishers.
Borges-Nojosa, DM, Cascon, P (2005): Herpetofauna da Área                Loebmann, D., Haddad, C.F.B. (2010): Amphibians and reptiles
   Reserva da Serra das Almas, Ceará. - In: Araújo, FS, Rodal, MJN,         from a highly diverse area of the Caatinga domain: composition
   Barbosa, MRV (Eds.). Análise das Variações da Biodiversidade             and conservation implications. Biota Neotropica 10: 227-256.
   do Bioma Caatinga. Brasília, Ministério do Meio Ambiente,             Magurran, A.E. (2011): Measuring Biological Diversity. Malden,
   243-258pp.                                                               USA: Blackwell Publishing Company.
Cascon, P., Brito, L.B.M., Roberto, J.I. (2014): Anfíbios. In: Botero,   Oliveira, G., Diniz-Filho, J.A.F. (2010): Spatial patterns of ter-
   J.I.S., Garcez, D.S. Anfíbios e Peixes do Parque Nacional de             restrial vertebrates richness in Brazilian semiarid, Northeastern
   Ubajara e Entorno, Fortaleza, LABOMAR. 128pp.                            Brazil: Selecting hypotheses and revealing constraints. Journal
Cascon, P. (1987): Observações sobre diversidade, ecologia e re-            of Arid Environments 74: 1418-1426.
   produção na anurofauna de uma área de Caatinga. Dissertação           R Development Core Team. (2013): R: A language and environ-
   de Mestrado. Universidade Federal da Paraíba, Departamento               ment for statistical computing. R Foundation for Statistical
   de Biologia, Mestrado em Zoologia.                                       Computing.
Cascon, P., Langguth, A. (2016). Composition, reproduction and           Ribeiro, S.C., Roberto, I.J., Sales. D.L., Ávila, R.W., Almeida,
   ecological aspects of a Caatinga anurofauna in Paraiba State,            W.O. (2012): Amphibians and Reptiles from the Araripe biore-
   Brazil. Revista Nordestina de Biologia 24:23-66.                         gion, northeastern Brazil. Salamandra 48: 133-146.
Chesson, P., Gebauer, R.L.E., Schwinning, S., Huntly, N., Wi-            Roberto, I.J., Loebmann, D. (2016): Composition, distribution
   egand, K., Ernest, M.S.K., Sher, A., Novoplansky, A., Weltzin,           patterns, and conservation priority areas for the Herpetofauna
   J.F. (2004): Resource pulses, species interactions, and diversity        of the state of Ceará, northeastern Brazil. Salamandra 52: 134-
   maintenance in arid and semi-arid environments. Oecologia                152.
   141: 236-253.                                                         Santana, D.J., Mângia, S., Silveira-Filho, R.R., Barros, L.C.S.,
Colwell, R.K. (2005): Estimates, version 7.5: Statistical estimation        Andrade, I., Napoli, M.F., Juncá, F., Garda, A.A. (2015):
   of species richness and shared species from samples. Available           Anurans from the Middle Jaguaribe River Region, Ceará State,
   in: http://purl.oclc.org/estimates. Access: 17 of july of 2011.          Northeastern Brazil. Biota Neotropica 15: 1-8.
Duellman, W.E., Trueb, L. (1994): Biology of Amphibians. 2ª Ed.          Scott Jr., N. J., Woodward, B.D. (1994): Measuring Biological
   Washington: The Johns Hopkins University Press.                          Diversity Standard Methods for Amphibians. Washignton and
Duellman, W.E., Marion, A.B., Hedges, S.B., (2016): Phylogenet-             London, Smithsonian Institution. Surveys at breeding sites.
   ics, Classification, and Biogeography of the Treefrogs (Amphib-       Moura, G.J.B., Santos, E.M., Oliveira, M.A.B., Cabral, M.C.C.,
   ia: Anura: Arboranae). Zootaxa 4104: 001–109.                            Eds, Ibama.
Ferner, J.W. (2007) A review of marking and individual recognition       Silveira- Neto, S., Nakano, O., Barbin, D.,Nova, N.A.V. (1976):
   techniques for amphibian and reptiles. Herpetological Circular           Manual de Ecologia dos Insetos. São Paulo: Editora Agronômi-
   35. Society for the Study of Amphibians and Reptiles, Atlanta.           ca Ceres.
Frost, D.R. (2017): Amphibian Species of the World: an Online            Vieira, W.L.S., Arzabe, C., Santana, G.G. (2007): Composição e
   Reference. Version 6.0. Electronic Database accessible at: http://       distribuição espaço-temporal de anuros no Cariri Paraibano,
   research.amnh.org/herpetology/amphibia/index.html. American              Nordeste do Brasil. Oecologia Brasiliensis. 11: 383-396.
   Museu of Natural History, New York, USA.                              Ximenes, C.L. (2008): Tanques fossilíferos de Itapipoca, CE-
Funceme (2011): Gráficos de chuvas dos postos pluviométricos.               Bebedouros e cemitérios de megafauna pré-histórica. Sítios
   Available in: www.funceme.br/areas/monitoramento/grafico-                geológicos e paleontológicos do Brasil. Available at: www.unb.
   de-chuvas-dos-postos-pluviometricos. Access: 05 of september             br/ig/sigep/sitio014/sitio014.pdf
   of 2011.
Composition and diversity of anurans from rock outcrops, Brazil                               195
Appendix 1. Voucher list.

  The reference specimens can be found at
CHUFC under numbers Dendropsophus rubin-
cundulus: (CHUFCA5831), Leptodactylus fuscus:
(CHUFCA5820; CHUFCA5821), L. macrosternum:
(CHUFCA6170;      CHUFCA6171),      L.     vastus:
(CHUFCA6172;       CHUFCA6173),        Pithecopus
nordestinus: (CHUFCA6175), Physalaemus albifrons:
(CHUFCA6181;      CHUFCA6182),       Pleurodema
diplolister:   (CHUFCA6176;      CHUFCA6177),
Proceratophrys     cristiceps:   (CHUFCA6179;
CHUFCA6180),      Pseudopaludicola    mystacalis:
(CHUFCA5837; CHUFCA5838), Rhinella granulosa:
(CHUFCA6168; CHUFCA6169), Scinax x-signatus:
(CHUFCA6165; CHUFCA6166).

                                                                  Accepted by Cynthia Prado
You can also read
Next slide ... Cancel